Book contents
- Frontmatter
- Contents
- List of contributors
- Preface
- 1 Effects of climate change on fungal diseases of trees
- 2 Effects of climate change on Fusarium foot rot of winter wheat in the United Kingdom
- 3 Effects of UV-B radiation (280–320 nm) on foliar saprotrophs and pathogens
- 4 Implications of global warming and rising sea-levels for macrofungi in UK dune systems
- 5 Red Data Lists and decline in fruiting of macromycetes in relation to pollution and loss of habitat
- 6 Effects of dry-deposited SO2 and sulphite on saprotrophic fungi and decomposition of tree leaf litter
- 7 Effects of atmospheric pollutants on phyllosphere and endophytic fungi
- 8 Influences of acid mist and ozone on the fluorescein diacetate activity of leaf litter
- 9 Mycorrhizas and environmental stress
- 10 Myccorhizas, succession, and the rehabilitation of deforested lands in the humid tropics
- 11 Potential effects on the soil mycoflora of changes in the UK agricultural policy for upland grasslands
- 12 Uptake and immobilization of caesium in UK grassland and forest soils by fungi, following the Chernobyl accident
- 13 Effects of pollutants on aquatic hyphomycetes colonizing leaf material in freshwaters
- 14 Fungi and salt stress
- 15 Fungal sequestration, mobilization and transformation of metals and metalloids
- 16 Urban, industrial and agricultural effects on lichens
- 17 Fungal interactions with metals and radionuclides for environmental bioremediation
- 18 Impact of genetically-modified microorganisms on the terrestrial microbiota including fungi
- 19 Has chaos theory a place in environmental mycology?
- Index of generic and specific names
- Subject index
3 - Effects of UV-B radiation (280–320 nm) on foliar saprotrophs and pathogens
Published online by Cambridge University Press: 05 November 2011
- Frontmatter
- Contents
- List of contributors
- Preface
- 1 Effects of climate change on fungal diseases of trees
- 2 Effects of climate change on Fusarium foot rot of winter wheat in the United Kingdom
- 3 Effects of UV-B radiation (280–320 nm) on foliar saprotrophs and pathogens
- 4 Implications of global warming and rising sea-levels for macrofungi in UK dune systems
- 5 Red Data Lists and decline in fruiting of macromycetes in relation to pollution and loss of habitat
- 6 Effects of dry-deposited SO2 and sulphite on saprotrophic fungi and decomposition of tree leaf litter
- 7 Effects of atmospheric pollutants on phyllosphere and endophytic fungi
- 8 Influences of acid mist and ozone on the fluorescein diacetate activity of leaf litter
- 9 Mycorrhizas and environmental stress
- 10 Myccorhizas, succession, and the rehabilitation of deforested lands in the humid tropics
- 11 Potential effects on the soil mycoflora of changes in the UK agricultural policy for upland grasslands
- 12 Uptake and immobilization of caesium in UK grassland and forest soils by fungi, following the Chernobyl accident
- 13 Effects of pollutants on aquatic hyphomycetes colonizing leaf material in freshwaters
- 14 Fungi and salt stress
- 15 Fungal sequestration, mobilization and transformation of metals and metalloids
- 16 Urban, industrial and agricultural effects on lichens
- 17 Fungal interactions with metals and radionuclides for environmental bioremediation
- 18 Impact of genetically-modified microorganisms on the terrestrial microbiota including fungi
- 19 Has chaos theory a place in environmental mycology?
- Index of generic and specific names
- Subject index
Summary
Ozone (O3), ultra-violet (UV) radiation and climate change
The earth's atmosphere contains about 3 nl l-1 O3, that fraction being continuously turned over. Approximately 10% is dispersed in the troposphere, which extends 15 km above the ground, and 90% in the stratosphere, which extends up to 50 km. While man's activities are causing some increase in tropospheric O3, mainly around major urban areas, they are depleting stratospheric O3 on a global scale (Anon., 1993a,b). Depletion occurs because of the release of chlorine-containing compounds, such as chlorofluorocarbons and carbon tetrachloride, that promote O3 breakdown.
Solar radiation includes wavelengths as short as 200 nm but that below approximately 290 nm is absorbed in the atmosphere, mainly by O3. Since energy per quantum of radiation increases as wavelength decreases, O3 protects organisms from the most energy-rich, and potentially most damaging, wavelengths in solar radiation. The efficiency with which ozone absorbs UV decreases as wavelength increases, so progressive thinning of the O3 layer will allow shorter wavelengths to reach the earth's surface as well as allowing higher fluxes to be transmitted of the wavelengths already penetrating. It is significant that the cut-off wavelength is not constant but varies with season and time of day. For example, in Reading, England (51.5° N), the shortest detectable wavelength varied from 302 nm in January to 294 nm in July, and from 294 nm at noon to 300 nm at 17.00 hours in July (Anon., 1993b).
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- Fungi and Environmental Change , pp. 32 - 50Publisher: Cambridge University PressPrint publication year: 1996
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